38
Organized by 统筹: The Hong Kong Bird Watching Society The International Black-faced Spoonbill Census 2016 The Hong Kong Bird Watching Society 香港观鸟会 BirdLife International Asia Division

The International Black-faced · Liu Dan Yang 刘 丹阳, Liu Jun 刘 ... Zhang Yan 张嫣, Zheng Kanghua 郑康华, Zheng Se Xin 郑色鑫, Zheng Xi ... 陈柏均 Chen Po Chun, 吴世鸿

  • Upload
    hatuong

  • View
    238

  • Download
    0

Embed Size (px)

Citation preview

Organized by 统筹:

The Hong Kong Bird

Watching Society

The International Black-faced

Spoonbill Census 2016

脸 鹭

The Hong Kong Bird Watching Society

香港观鸟会

BirdLife International

Asia Division

The International Black-faced Spoonbill Census 2016

Copyright

The Hong Kong Bird Watching Society. All rights reserved.

The publisher hereby gives permission to teachers, students, educational institutions, research

institutions, conservation organizations and the media to make use of short extracts of the text and also

charts in this publication for non-commercial, educational, scientific and conservation purpose,

provided always that due acknowledgement is given and that a copy of the work containing such

extracts and charts is sent to the publisher for record.

Published by

The Hong Kong Bird Watching Society

BirdLife International Partner

Available from

The Hong Kong Bird Watching Society

7C, V Ga Building,

532 Castle Peak Road,

Lai Chi Kok, Kowloon, Hong Kong

Postal address: G.P.O. Box 12460, Hong Kong

Tel: (852) 2377 4387 Fax: (852) 2314 3687

E-mail: [email protected] Website: www.hkbws.org.hk

Recommended citation

Yu, Y.T, Fong, H.H.N. and Tse, I.W.L. 2016. International Black-faced Spoonbill Census 2016. Black-

faced Spoonbill Research Group, The Hong Kong Bird Watching Society. Hong Kong.

Cover photo

Black-faced Spoonbills Platalea minor at Cixi, Zhejiang.

Credited by Qian Bin, Zhejiang Wild Bird Society

2

The International Black-faced Spoonbill Census 2016

Coordinator

Yat-tung Yu

The Hong Kong Bird Watching Society

Data contributors

(Republic of Korea 韩国) Keonseok Park, Ji Nam-Joon, Kang Chang-Wan,Kang Hee-Man Kim Eun-Mi,

Oh Mi-Rae, Jeju Wildlife Research Center (Mainland China and Hainan 中国大陆及海南岛) Bo Biao 卜

标, Bo Yi Fan 卜一凡, Ceng Li Man 曾立满, Ceng Qing Jie 曾庆阶, Ceng Xiangwu 曾向武, Chen Chun

Xiang 陈春香, Chen Junteng 陈俊腾, Chen Qiong Fa 陈琼发, Chen Shi Qian 陈世倩, Chen Si Tu 陈斯图,

Chen Shirong 陈施容, Chen Yi Juan 陈亦隽, Chen Yu Xuan 陈语暄, Chen Yuan Xin 陈源鑫, Chen

Zhihong 陈志鸿, Chen Zi Lin 陈紫琳, Cheng Cheng 程成, Cui Tenghui 崔腾辉, Deng Xiaolong 邓小龙,

Du Jia Yin 杜嘉胤, Guo Jungong 郭竣工, Hu Weining 胡伟宁, Huang Qi Feng 黄启锋, Huang Wen Ming

黄文铭, Huang Xueding 黄学鼎, Ke Rui 柯睿, Li An Jing 李安静, Li Fanghua 李芳华, Li Fei 李飞, Li Jie

黎捷, Li Wen Hao 李文灏, Li Qiao Qiao 李巧巧, Li Xiao Xia 黎晓霞, Li Yao 李尧, Li Ying Wen 李近文,

Li Yu Hang 李字航, Liang Qiaoyi 梁俏仪, Liao Feng 廖烽, Lin Guangxuan 林广旋, Lin Siming 林思明,

Liu Dan Yang 刘丹阳, Liu Jun 刘军, Liu Hao Xiang 刘浩翔, Liu Qi Bang 刘启邦, Liu Yi Ming 刘一鸣,

Lu Gang 卢刚, Lu Yi Zhang 陆益彰, Mou Zhe 缪喆, Ni Guanghui 倪光辉, Ouyang Li Hong 欧阳丽洪,

Pan Bing Zhen 潘柄臻, Pan Neng Qian 潘能干, Pang Yong Xiong 庞永雄, Peng Zi Quan 彭梓铨, Qian

Bin 钱斌, Quan Shengyi 全胜义, Ruan Yi Jun 阮一骏, Sun Renjie 孙仁杰, Tsim Siu Tai 詹肇泰, Wang Bo

王柏, Wang Hai Yan 王海燕, Wang Shang 王上, Wang Shuai 王帅, Wang Yi Jun 王宜君, Wei Jian Xian

魏健贤, Wen Bi Lin 温壁粼, Wu Kan Song 吴坎宋, Xie Qiao 谢乔, Xu Zi Xuan 徐子轩, Yang Jin 杨金,

Yang Wei Min 杨伟民, Yao Li 姚力, Ye Hai Jiang 叶海江, Ye Zhi Ying 叶志英, You Yu Bing 游宇冰,

Yuan Huaqian 袁化干, Zhang Fuqing 张福庆, Zhang Jiejun 张杰君, Zhang Junxuan 张俊轩, Zhang Kai

张凯, Zhang Lieni 张列妮, Zhang Lixing 张力行, Zhang Wei 张苇, Zhang Wen Yao 张文耀, Zhang

Xuling 张旭玲, Zhang Yan 张嫣, Zheng Kanghua 郑康华, Zheng Se Xin 郑色鑫, Zheng Xi 郑玺, Zhong

Huien 钟辉恩, Zhong Jing Zhen 钟静贞, Zhong Qiao 钟薇, Zhong Zhiqiang 钟志强, Zhu Jun An 朱俊

安, Zhu Tian Yi 朱天一, Zhuang Jun 庄珺, Zhuang Weimin 庄伟民, Yu Hai Yan 虞海燕, Yu Zi Han 余

子涵 Zhuhai Bird Watching Society 珠海市观鸟协会, Shenzhen Bird Watching Society 深圳市观鸟协会,

Hainan Wildlife Conservation Bureau 海南省林业局野生动植物保护管理局 , Putian Bird Watching

Society 莆田观鸟会 , Kadoorie Farm & Botanic Garden 嘉道理农场暨植物园 , Fujian Bird Watching

Society 福建省观鸟会, Wild Bird Society of Shanghai 上海野鸟会, Zhejiang Wild Bird Society 浙江野鸟

会, Guangdong Hafieng Gongping Daihu Provincial Nature Reserve Office 广东海丰公平大湖保护区辨

公室, South China Institute of Endangered Animals 华南濒危动物研究所, Fujian Wildlife and Wetland

Resources Monitoring Centre 福建省野生动植物与湿地资源监测中心 and Zhanjiang Mangrove National

Nature Reserve 湛江红树林国家级自然保护区 . (Japan 日本 ) Shigeru Tokumoto 徳元茂 , Satoru

Nakagome 中込哲, Toru Watanabe 渡辺彻, Shoji Tashiro 田代省二, Kimiko Kouno 河野纪美子, Chiaki

Kishihara 岸原千秋, Sumiko Tanabe 田辺スミ子, Satoru Matsuomoto 松元悟, Masuko Kinoshita 木下マ

3

ス子, Hiroto Okabe 冈部海都 , 32 BFS census event participants BFS 调査イベント参加者 32 名, Kzuhisa

Oue 尾上和久, Makoto Tominaga 冨永诚, Satoru Matsumoto 松元悟, Yasuo Miyazaki 宫崎八州雄, Reiko

Fukushima 福嶋玲子, Seizaburoh Yasuo 安尾征三郎, Tadashi Toyoshima 豊岛正, Junichi Yoshida 吉田

顺一, Masayo Hoshi 星昌代, Makoto Nishi 西村诚, Miyako Kato 迦统美阳子, Mitsuo Iwaihara 祝原光雄,

Minoru Mitsuda 満田实 , Kanroku Aoyama 青山寛六 , Kotaro Okamoto 冈本浩太朗 , Yoshifumi

Matsumoto 松元芳文, Takashi Asada 浅田骏, Junichi Maeda 前田润一, Hiroshi Okamoto 冈本浩士, Ken-

ichi Shiraishi 白石健一, Hiroshi Mitsunaga 光永汪, Yasuko Kano 嘉野康子, Syoko Nakahara 中原菖子,

Kenzaburo Inoue 井上贤三郎, Syoko Nakahara 中原菖子, Atsuhito Hamasuna 滨砂淳人, Saori Hamasuna

滨砂沙织 Kazunori Yamamoto 山本和纪, Shigeki Takano 高野茂树, Tatsuo Yamada, Kajiko Yamada,

Naoto Togano 栂野直人, Syuji Yoshida 吉田秀治, Hiroshi Yamaguchi 山口广, Hiroko Yamaguchi 山口宏

子, Yasuhiro Ide 井手保宏, Shinichi Yoshida 吉田新一, Satoshi Nakahara 中原聡, Kazuhiro Maeda 前田和

浩, Keiko Miyano 宫野启子, Hiroshi Kukita 久木田纮, Kusunoki Shizenkan くすの木自然馆, Fumio

Mizogichi 沟口文男, Tsukasa Kamimura 上村司, Takako Morikawa 森河贵子, Takashi Morikawa 森河隆

史 , Kazuhiko Nagaya 长屋和彦 , Yohei Kurosaka 黒坂洋平 , Sayaka Miyagi 宫城さやか , Masakuni

Yamashiro 山城正邦, Kozo Hashimoto 桥本幸三, Kamenobu Ooshiro 大城亀信, Yutaka Toguchi 渡久地

豊, Michio Kanashiro 金城道夫,. (Taiwan 台湾) 蔡世鹏 Tsai Shih Peng, 邱柏莹 Chiu Po Ying, 张弘和

Chang Hung Ho, 郭东辉 Kuo Tung Hui, 李裕仁 Li Yu Jen, 杨秀銮 Yang Shiu Luan, 黄礼仪 Huang Li

Yi, 王国兴 Wang Kuo Hsing, 李真明 Li Chen Ming, 王征吉 Wang Cheng Chi, 吴丰进 Wu Feng Chin,

徐幸玉 Hsu Hsing Yu, 林传贵 Lin Chuan Kuei, 陈美月 Chen Mei Yueh, 郑翠凤 Cheng Tsui Feng, 颜

泓澈 Yen Hung Che, 杨淑萍 Yang Shu Ping, 何一先 Ho Yi Hsien, 吕翊维 Lu I Wei, 吴豫州 Wu Yu-

Chou, 陈谓熊 Chen Wei Hsiung, 洪维锋 Hung Wei Feng, 陈琗瑢 Chen Tsui Jung, 刘春凤 Liu Chun

Feng, 张世鸿 Chang Shih Hung, 李益鑫 Li Yi-Hsin, 黄瑞政 Huang Jui Cheng, 黄圣扬 Ho Kuo Chen,

何国琛 Hsiao Shun Chang, 萧舜昌 Liu Te-Sheng, 刘得升 Tsai Shih Peng, 蔡世鹏 Chen Yi Chi, 陈奕

锜 Chen Yi Chi, 钟上玮 Chung Shang Wei, 林生州 Lin Sheng Chou, 罗瑞焜 Lo ui Kun, 罗美玉 Lo Mei

Yueh, 陈英俊 Chen Ying Chun, 吴自强 Wu Tzu Chiang, 萧云杰 Hsiao Yun Chieh, 王振芳 Wang

Chen Fang, 陈雪琴 Chen Hsueh Chin, 吴丽兰 Wu Li Lan, 杨育宽 Yang Yu Kuan, 李文化 Li Wen Hua,

林昆海 Lin Kun Hai, 吴世鸿 Wu Shih Hung, 陈俊强 Chen Chun Chiang, 吴正文 Wu Cheng Wen, 胡

林志 Huang Lin Chih, 洪慧意 Hung Hui Yi, 石明卿 Shih Ming Ching, 刘庆文 Liu Ching Wen, 黄家发

Huang Jia Fa, 施励强 Shih Li Chiang, 罗英昌 Lo Ying Chang, 王克孝 Wang Ko Hsiao, 苏汉江 Su Han

Chiang, 林国钦 Lin Kuo Chin, 苏俊荣 Su Chung Jung, 彭靖坚 Peng Ching Chien, 陈戎琛 Chen Jung

Chen, 庄西进 Chuang His Chin, 陈秀竹 Chen Hsiu Chu, 洪清漳 Hung Ching Chang, 王建华 Wang

Chieh Hua, 郑谦逊 Cheng Chien Hsun, 汪雨新Wang Yu Hsin, 曾惠珠 Tseng Hui Chu, 戴子尧 Tai Tzu

Yao, 王玉秀 Wang Yu Shiu, 蔡文凯 Tsai Wen Kai, 陈柏均 Chen Po Chun, 吴世鸿 Wu Shih Hung, 郭

忠诚 Kuo Jong Cheng, 严馨斌 Yan Xin Bin, 陈建诚 Chen Jian Cheng, 郭兰贞 Kuo Lan Chen, 章文刚

Chang Wen Kang, 蔡青芠 Tsai Ching Wen, 蔡嘉峰 Tsai Chia Feng, 邱彩绸 Chiu Tsai Chou, 蔡俊南

Tsai Chun Nan, 念荣汉 Nien Jung Han, 黄南铭 Huang Nan Ming, 戴炎文 Tai Yen Wen, 吴崇祥

Wu Chung Hsiang, 郑和泰 Cheng Huo Tai, 黄永丰 Huang Yung Feng, 邱景威 Chiu Ching Wei, 邱仁

武 Chiu Jen Wu, 黄光瀛 Huang Kuan Ying, 蔡金助 Tsai Chin Chu, 李明华 Li Ming Hua,陈尚钦 Chen

4

Shang Chin, 黄明达 Huang Ming Ta, 洪登富 Hung Teng Fu, 蔡乙荣 Tsai Yi Jung, 李昶诚 Li Chang

Cheng, 黄议新 Huang Yi Hsin, 黄千瑄 Huang Chien Hsuan, 黄怡程 Huang Yi Cheng, 黄俊德 Huang

Chin Te, 陈惠玲 Chen Hui Ling, 辜朝柏 Kuo Chao Po, 宋绍民 Sung Shao Min, 黄照中 Huang Chao

Chung, Black-Faced Spoonbill Conservation Association 台湾黑面琵鹭保育学会, Chiehting Ecological

and Cultural Association, Kaohsiung 茄萣生态文化协会, Chinese Wild Bird Federation 社团法人中华民

国野鸟学会 , Ecological Conservation Association of Chai-Yi County 嘉义县生态保育协会 , Kenting

National Park 垦丁国家公园管理处, Kinmen National Park, 金门国家公园管理处, Marine National Park

海洋国家公园管理处, National University of Tainan 国立台南大学, Taijiang National Park 台江国家公园

管理处, Tainan Ecological Conservation Association 台南市生态保育协会, The, Nature & Ecology Society

of Miao Li 苗栗县自然生态学会, Wild Bird Association of Taiwan 社团法人台湾省野鸟协会, Wild Bird

Society of Changhwa 彰化县野鸟学会, Wild Bird Society of Chiayi 嘉义市野鸟学会, Wild Bird Society of

Hsinchu 新竹市野鸟学会, Wild Bird Society of Hualien 社团法人花莲县野鸟学会, Wild Bird Society of I-

Lan 宜兰县野鸟学会, Wild Bird Society of Kaohsiung 社团法人高雄市野鸟学会, Wild Bird Society of

Kimen 社团法人金门县野鸟学会, Wild Bird Society of Matsu 马祖县野鸟学会, Wild Bird Society of Peng-

Hu 澎湖县野鸟学会, Wild Bird Society of Pingtung 屏东县野鸟学会, Wild Bird Society of Tainan 社团法

人台南市野鸟学会, Wild Bird Society of Taipei 台北市野鸟学会, Wild Bird Society of Taitung 台东县野

鸟学会, Wild Bird Society of Taoyuan 桃园市管理处野鸟学会 and Wild Bird Society of Yunlin 云林县野

鸟学会 及上述鸟会之志愿调查员 and volunteer surveyors of the societies above. (Hong Kong 香港) Ho

Chun Hung 何振雄, 黄威娜, 黄锦文, Leung Chui Shing Evans 梁钊成, Alex Ng Wing Chuen, Chan Tak

Sum, 刘康乔, Wong Hok Sze 王学思, 王乐容, 王子杰, 江珀墉, Wong Hing Fat Benjamin, Chang Chi Wai,

吴志强, Alvin Hui 许桓峰, Cecilia Kwan 关小春, Li Siu Lan 李笑兰, Leung Hau Kin 梁厚键, Cheung

Wing Yu, Tang Fuk Ka 邓伏珈, Chan Wing Kwan 陈颖君, Chan Man Ho 陈文灏, Yip Yuen Ming 叶婉明,

Law Chun Wan, Chris Lam, 蔡美贞, Li Wing, Chan Kam Nga, Ma Yat Man Watter 马逸文, Tang Kam

Ming 邓锦明, Wong Hing Fat Benjamin, Chau Sau Yu, 高家浩, 林栢坚, Wong Ching Man, 洪国基, 陈启

昌, Cheng Wai Keung 郑伟强, Ying Hak King 英克劲, Austin NG 吴文正, Ho Siu Chun, AEC Ltd. and

Agriculture, Fisheries and Conservation Department 渔农自然护理署. (Macao 澳门) Chan Sot 陈述, Chan

U Heng 陈儒兴, Fong Ka Chon 方嘉俊, Hoi Hin U 许轩渝, Tam, Kam Heng 谭金庆, Lei Kam Peng 李

金平, Choi Cheng A, 蔡静亚, Yeung Chun Yu 杨镇宇, Tam Wing Keung 谭永强, Leung Va 梁华, Civic

and Municipal Affairs Bureau 民政总署, Environmental Protection Bureau 环境保护局 and Macau Aves

Society 澳门鸟会. (Vietnam 越南) Thuy, Le Trong Trai and Paul Insua-Cao, Viet Nature Conservation

Centre and Xuan Thuy National Park. (The Philippines 菲律宾) Mike Lu, Josiah David Quimpo and

Wild Bird Club of the Philippines. (Cambodia 柬埔寨) Vorsak Bou and Birdlife Cambodia. (Thailand 泰

国) Uaiphorn Khwanphae and Bird Conservation Society of Thailand.

5

The International Black-faced Spoonbill Census

2016

黑脸琵鹭全球同步普查 2016

English Report

英文报告

6

The International Black-faced Spoonbill Census 2016

Yat-tung Yu, Helen H.N. Fong and Ivan W.L. Tse

Black-faced Spoonbill Research Group,

The Hong Kong Bird Watching Society

Abstract

The annual International Black-faced Spoonbill Census has been proven to be an

effective method to provide comparable figures and distribution of this endangered

intertidal waterbirds for assessing its population health. The 2016 International Census

was conducted on 15-17 January 2016, covering the area from Korea and Japan in the

north to Thailand and the Philippines in the south. The result is a total of 3,356 Black-

faced Spoonbills counted in this period, being the highest figure for this species since

the inception of this census in the early 1990s. The three largest congregation sites of

this species are Tsengwen estuary area in Tainan (963 individuals), Bazheng estuary

area in Chiayi (782 individuals) and Deep Bay between Hong Kong and Shenzhen (371

individuals), while the first two sites are only 30km apart. The numbers recorded in

Taiwan, mainland China and Japan increased, while declines of numbers were found

in Deep Bay and the Red River Delta of Vietnam.

Introduction

Black-faced Spoonbill Platalea minor is listed as a globally endangered from its very

small population, which is expected to undergo a continuing decline in near future

owing primarily to the loss of habitat to industrial development, land reclamation and

pollution (BirdLife International 2015). This species inhabits along the coastal areas on

the eastern fringe of Asia (Hancock et al. 1992, del Hoyo et al. 1992, Yu and Swennen

2004, BirdLife International 2015). In early 1990s, this species, with fewer than 300

individuals, confined to a few sites in the East Asian region (Kennerley 1990), and

drew the attention of conservationists. Subsequently, this annual census was

inaugurated in 1993 to assess the wintering population of Black-faced Spoonbill. Since

then, the wintering population was found to be recovering through natural population

expansion and conservation efforts in some of the sites. The number of individuals

recorded has exceeded 1,000 since 2003 (Yu 2003), soaring further to over 2,000 since

2009, with an exception in 2011 (Chan & Yu 2012).

7

This annual census is of high priority in the conservation plans of this endangered

species (Severinghaus et al. 1995, Chan et al. 2010) because it has been proven to be an

effective means to gather annual figures of the population and distribution of

wintering Black-faced Spoonbills through international collaboration. The Hong Kong

Bird Watching Society began to spearhead this census from 2003 onwards. This report

aims to present the results of the census undertaken in January of 2016.

Method

Past censuses were unanimously held in mid-winter when the wintering population

of spoonbills apparently remained stable. The dates scheduled for the censuses usually

coincided with the dates of high tides in the Red River Delta in Vietnam and Deep Bay

between Hong Kong and Shenzhen, given that high tide facilitates the counting in

these sites. In 2016, the census period was scheduled on 15-17 January 2016. Sites with

Black-faced Spoonbills recorded during the census are shown in map 1. Guidelines on

the technical basis were sent to the surveyors in advance of the census. Most of the

field counts were done within the census period. For some sites in close proximity such

as Mai Po in Hong Kong and Futian in Shenzhen in the Deep Bay area, where the

spoonbills can fly between these sites within an hour, counts were conducted at the

two sites simultaneously. All the counts in the census were made with binoculars and

telescopes.

Census depends on the volunteer work by the local birdwatchers, conservationists,

researchers, ornithologists and reserve officers. Census results were summarized by

coordinators in the respective regions or individual surveyors before transmission to

the international coordinator for in-depth analysis and announcement.

Results and discussion

Overview

This census in 2016 recorded a total of 3,356 Black-faced Spoonbills in the East Asia

region where all records were along the coast. This figure accounts for a growth of 84

individuals (2.6%) from the census in 2015 (table 1 and 9). The annual population

change is in an average of 11% increase since 1989 (table 9). Changes in different

wintering areas are discussed below. The wintering Black-faced Spoonbills were found

in 68 sites in this census, 6 more sites than that in census of 2015.

8

Taiwan

2016: 2,060 birds

Taiwan is the largest wintering ground of Black-faced Spoonbills in the world and the

figure of 2016 retains this status (figure 2). A total of 2,060 individuals recorded in

Taiwan (including Penghu and Kinmen Counties) demonstrates an increase of 1.3%

from that of the previous year (2,034 individuals). Among these individuals, 963 birds

were recorded in the area of Tsengwen River estuary at the Tainan City, including

places as Chi-ku, Sicao and Tucheng; followed by 782 wintering Black-faced

Spoonbills at Bazheng River estuary at the boundary of Chiayi and 186 at Kaoshiung,

indicating the emergence of other large congregation sites from the original

assemblage site at Tsengwen River estuary. Smaller groups were scattered in other

parts of Taiwan, including Taipei, Eastern and Central parts of Taiwan, and the

outlying islands. More details of the counts in Taiwan are available in tables 1, 2 and

3.

Pearl River Estuary (including Deep Bay between Hong Kong and Shenzhen,

Taipa-Coloane in Macao)

2016: 432 birds, including 371 birds in Deep Bay and 61 birds in Taipa-Coloane wetland

The number of wintering Black-faced Spoonbills in the Pearl River Estuary decreased

in 2016 again, despite to an increase recorded in 2015. The decrease is mainly attributed

by a dropping number of birds in the Deep Bay area, where a total of 371 birds were

present in 2016, showing a drop of 9.7% from the previous year. Same as in the

previous censuses, the latest census in the Deep Bay area covered various sites

including Mai Po Nature Reserve, Lok Ma Chau, Tsim Bei Tsui intertidal area, Hong

Kong Wetland Park and Futian National Nature Reserve in Shenzhen. The figure of

Deep Bay represents 11% of the global wintering population in 2016, retains a level of

more than 10% of global population.

At Macao, 61 birds were counted in Taipa-Coloane wetland during the census in 2016

showing an increase of 10.9% from the previous year. The figure represents 1.8% of

the global wintering population this year. The feeding area of these birds is still

uncertain, although there were some sighting records in Heqing near Macao (5

individuals recorded in Heqing, but maybe the same flock of Macao birds). This

wintering site has been deteriorating due to the development of tourism industry,

making conservation of this spoonbill’s site difficult.

9

Mainland China and Hainan Island

2016: 434 birds

The number of wintering Black-faced Spoonbills in mainland China (including Hainan

Island) fluctuated in recent years. In the 2016 census, a count of 434 Black-faced

Spoonbills was recorded in this area, being an increase of 32% from the previous year

(table 5) and also a new high figure for mainland China in this census. This figure

represents 12.9% of the global population in 2016.

Two large wintering flocks were recorded: 122 individuals at Xinhua Bay and 144

individuals at Haifeng, the latter being the largest wintering flock in mainland China.

Several new wintering sites were found in Eastern China including Fujian County and

Zhejiang County in this winter, some of those had Black-faced Spoonbill recorded

during census period. The new sites were including 38 individuals recorded at

Luoyuan Bay on 17 Jan and 8 birds recorded at Hangzhou Bay on 19 Jan. The new

wintering sites may be a result of natural dispersion of Black-faced Spoonbill or the

habitat decline of original wintering site. More study and survey in mainland China

would be suggested to do for long term monitoring and conservation.

Red River Delta, Vietnam

2016: 9 birds

Nine Black-faced Spoonbills were recorded in the Red River Delta in 2016, having a

decrease of 77.5% from 2015 (44 birds). The actual number in this area might be higher,

as disturbances in this site were noted in the same week of the census. Same as in the

past censuses, most birds were recorded in the Xuan Thuy area in the Red River Delta.

The wintering population trend at Red River Delta did not match with the global one

and showed a decreasing trend, with high numbers occasionally recorded in the past

(e.g. 75 individuals in 1995-96).

Japan

2016: 383 birds

A total of 383 individuals were recorded in 40 sites (table 1), representing 11.4% of the

global population in this census. It also had an increase of 3.2% from 2015 and being a

new high figure for Japan (table 7). Kumamoto Prefecture held the largest flock (127

individuals) of the wintering Black-faced Spoonbills, including 44 birds at Kagami

River estuary and 21 birds in the area of Uki City, Ohno River estuary and Suna River

estuary.

10

Republic of Korea

2016: 38 birds

Jeju Island is a main wintering site of the Black-faced Spoonbill in South Korea, this

census had a record of 38 birds (23 at Hado-ri and 15 at Seongsanpo). This total

represented 1.1% of the global population and had an increase of 23% from that of the

2015 (31 individuals). Besides, there was a single bird recorded near Seosan City

outside the census period.

[The Philippines

2016: 0 (1 bird outside census period)

None was reported during the census period but single was recorded on 14 Jan 2016.

Small numbers of the Black-faced Spoonbill were recorded irregularly in recent years.

Survey coverage for the wintering Black-faced Spoonbills and other waterbirds was

still low in the Philippines.]

[Thailand

2016: 0

None was reported in winter 2015-16, though small numbers, especially young birds,

were found in the Inner Gulf of Thailand in previous years.]

Conclusion

The wintering Black-faced Spoonbill population had a very mild increase of 2.5%

recorded in this census. The global population is generally increasing (in 11% annually)

since the commencement of this census in 1993, except a few winters (e.g. 2009 and

2011). However, it does not apply to individual sites. Tainan area has a similar trend

to the global population and the number in Japan increases too, while Deep Bay and

Red River Delta had decreases in the past 10 years. Sites along the coast of mainland

China had mixed trends.

Few sites have been implementing habitat management practices benefiting to Black-

faced Spoonbill and/or other waterbirds. Given that the population trend of Black-

faced Spoonbill is increasing, there is a need of increase of the total wetland capacity,

in order to have more and bigger sites for accommodating a larger population Black-

faced Spoonbills in the future. It is suggested that wetland management practices

should be considered, planned and implemented in wetlands within the distribution

range of Black-faced Spoonbills, especially sites with decreasing numbers of birds to

reverse the adverse situation, and/or sites with potentials to support more birds.

11

Hopefully, this will further secure long term survival of the Black-faced Spoonbill.

At present, the decrease of Black-faced Spoonbills in the Deep Bay area is of global

conservation concern. The Mai Po Inner Deep Bay Ramsar Site has been well managed

in order to support more Black-faced Spoonbills and other waterbirds. Conservation

practices have been applied to the site, such as improving loafing and roosting sites

condition and draining of fishponds and gei wai (i.e. traditional shrimp ponds) to

provide more feeding habitats. Therefore the reasons for declines of wintering Black-

faced Spoonbills at Deep Bay are still largely unknown, it might hamper the recovery

of the global Black-faced Spoonbill population and researches of spoonbill’s habitat

utilization in the Deep Bay area are suggested.

The population figures are different in every year, “1% population level” was defined

as the average of the figures from the last five years, 30 individuals out of 2,954

individuals. Site with more than 30 Black-faced Spoonbills could therefore be

suggested as important sites for this species and these sites included:

Tsengwen River estuary, Tainan City, Taiwan – 963 birds in 2016 (28.7%),

Bazhang River estuary in Southern Chiayi and Northern Tainan, Taiwan – 782

birds in 2016 (23.3%),

Deep Bay, Hong Kong and Shenzhen – 371 birds in 2016 (11.1%),

Kaoshiung, Taiwan – 186 birds in 2016 (5.5%),

Haifeng, Guangdong – 144 birds in 2016 (4.3%),

Xinhua Bay, Fujian – 122 birds in 2016 (4.1%),

Aogu Wetland, Taiwan – 88 birds in 2016 (2.7%),

Taipa-coloane wetland, Macao – 61 birds in 2016 (1.6%),

Sigang, Changhua River estuary, Hainan – 47 birds in 2016 (1.4%),

Kagami River estuary, Kumamoto, Japan – 44 birds in 2016 (1.3%),

*Luoyuan Bay, Fujian – 38 birds in 2016 (1.1%),

*Yinhu Bay, Guangdong – 31 birds in 2016 (1.0%).

Almost all the sites with more than 1% wintering population were included in all past

censuses, thereby allaying the chance of missing any considerable groups of wintering

Black-faced Spoonbills. The latter two sites (marked with asterisks above) were found

with more than 1% world population of the Black-faced Spoonbill from this census.

Therefore, it is suggested to conduct more surveys in these two sites in future to better

assess the actual populations of these sites and the trend.

12

The International Black-faced Spoonbill Census

2016

黑脸琵鹭全球同步普查 2016

Chinese Report

中文报告

13

黑脸琵鹭全球同步普查 2016

余日东 方海宁 谢伟麟

黑脸琵鹭研究组

香港观鸟会

撮要

黑脸琵鹭全球普查是一个搜集相类数据的重要途径,用以按年检视这种栖息于潮间带的

濒危水鸟的越冬种群的健康和分布状况。2016年度的黑脸琵鹭全球同步普查日期为2016

年 1 月 15-17 日,调查地区包括北至韩国、日本,南及泰国和菲律宾等地。2016 年共录

得 3,356 只黑脸琵鹭,是普查自 1990 年代初开展以来录得的新高。台南市曾文溪口(记

录到 963只)、嘉义县八掌溪口(记录到 782只)和香港与深圳间的后海湾(记录到 371 只),

是本年度调查结果所得的黑脸琵鹭三大度冬地点,当中八掌溪口及曾文溪口只相距 30

公里;黑脸琵鹭于台湾、中国大陆及日本的数字都有所上升,但是后海湾及越南红河口

的数字则有所下降。

引言

黑脸琵鹭 Platelea minor 种群细小,分布范围狭窄,加上生境受工业发展、土地开发及污

染等破坏,种群数量于可见的将来有下降的危机,因此被列入全球受胁鸟种名单

(BirdLife International 2015)。这个鸟种栖息于东亚沿海地区(Hancock et al. 1992, del

Hoyo et al. 1992, Yu and Swennen 2004, BirdLife International 2015)。于 1990 年代初

全球数目少于三百只,并仅在东亚几个地点录得,自此在保育方面受到广泛关注

(Kennerley 1990)。从 1993 年开始,全球同步普查于每年冬季进行,以评估黑脸琵鹭度

冬种群的状况。随着种群的自然增长和部份地点努力保育,度冬黑脸琵鹭的数量逐步上

升,在 2003 年突破 1,000 只(Yu 2003),自 2009 年开始(2011 年除外)更录得超过 2,000

只(Chan & Yu 2012)。

全球同步普查是黑脸琵鹭保育计划的优先项目(Severinghaus et al. 1995, Chan et al.

2010),这项国际协作调查已证实能有效提供度冬黑脸琵鹭的数量和分布数据。香港观鸟

会于 2003 年起统筹该全球同步普查。本报告会详述 2016 年 1 月普查的结果。

普查方法

过往的普查均选择于隆冬进行,皆因琵鹭数量于冬季中期显然较为稳定。普查进行的日

14

子,也必须是位于香港与深圳间的后海湾和越南春水(河口国家公园)潮涨的日子,因

为高涨的潮水有利数算工作。因此,2016 年的普查安排在 2016 年 1 月 15-17 日进行。

地图 1 显示了全球同步普查录得黑脸琵鹭的地点。在普查之前,本会向各调查员提供普

查指引作为技术基础。大部份的实地数算都是在普查期间进行,而部份地点如后海湾的

香港米埔和深圳福田相隔咫尺,琵鹭可于一小时内飞越两地,这些地点的数算工作有需

要同步进行。是次普查的所有数算工作均利用双筒和单筒望远镜进行。

琵鹭普查有赖各地资深观鸟者、保育工作者、研究员、鸟类学家和保护区内工作的官员

共同义务承担。各地的统筹员和个别的调查员收集和整理普查纪录后,将结果提交予国

际统筹员,作进一步的分析和结果公布。

结果及讨论

综观

2016 年的普查在东亚地区共录得 3,356 只黑脸琵鹭,主要在沿海一带录得,较 2015 年

普查录得的数目大幅上升了 84 只 (2.6%) (表 1 及 9)。分析往年的普查结果得出自 1989

年起,黑脸琵鹭的种群数目每年平均增幅为 11% (表 9)。于不同度冬地的详情会于下文

论述。2016 年的普查录得黑脸琵鹭于 68 个地点越冬,地点比往年多 6 个。

台湾

2016:2,060 只

台湾录得的度冬黑脸琵鹭数目一直是全球最多的(图 2),本年共录得 2,060 只度冬黑脸

琵鹭 (其中包括彭湖及金门县),比 2015 年(2,034 只)上升了 1.3%。其中,台南市曾文溪

口(包括七股、四草及土城等地)有全球最大的越冬黑脸琵鹭种群,总共录得 963 只,紧

接着的是嘉义县八掌溪口录得 782 只黑脸琵鹭。另一方面,高雄录得另一群为数 186 只

的度冬黑脸琵鹭,显示该两处成为曾文溪口以外的黑脸琵鹭集结地。台湾其他地点也分

别录得小群黑脸琵鹭,包括台北、东部、中部及外岛地区。有关台湾方面的调查,详情

可见表 1,2 和 3。

珠江河口(包括香港和深圳的后海湾,以及澳门凼仔路环)

2016:432 只,包括后海湾的 371 只以及路凼湿地的 61 只

珠江河口越冬的黑脸琵鹭数量在 2015 年的数量反弹之后,于 2016 年再次下降。数量下

降主要来自后海湾地区的数量显著下降,该地区本年只纪录得 371 只,较往年下降 9.7%。

一如过往的普查,这次调查覆盖后海湾地区多个地点,包括米埔自然保护区、落马洲鱼

塘、尖鼻咀潮汐带、香港湿地公园以及深圳福田自然保护区。2016 年普查在后海湾录得

的越冬黑脸琵鹭数目占全球度冬种群总数的 11%,维持在多于全球度冬种群 10%的水

平。

15

澳门方面,2016年的普查于路凼城生态保护区录得 61只黑脸琵鹭,较去年上升了 10.9%,

占全球越冬种群的 1.8%。虽然曾于附近的横琴有数个目击纪录(调查期间亦纪录到 5 只,

但极可能是部分澳门的种群),但此度冬种群的觅食区域仍然不明。然而,随着澳门旅游

业迅猛发展,黑脸琵鹭在当地的主要度冬地点外围环境恶化,令保护黑脸琵鹭在澳门的

度冬地点的情况仍然严峻。

中国大陆和海南岛

2016:434 只

近年来,中国大陆(包括海南岛)的黑脸琵鹭度冬种群数目变化较大,2016 年共录得 434

只,较去年上升了 32%(表 5),同时亦是于中国大陆度冬种群的新高,占 2016 年全球

越冬种群数量的 12.9%。

2016 年的调查中于中国大陆最大两个黑脸琵鹭越冬地是兴化湾 (122 只) 及海丰 (144

只) ,后者为 2016 年中国大陆最大的黑脸琵鹭度冬种群。今年冬天于中国东部的浙江及

福建发现数个新的黑脸琵鹭度冬地点,部分更于调查期间纪录到黑脸琵鹭。新的度冬地

点包括福建的罗源湾(于 1 月 17 日录得 38 只度冬黑脸琵鹭)及浙江的杭州湾(于 1 月 19

日录得 8 只度冬黑脸琵鹭)。新的度冬点可能是由于黑脸琵鹭的自然扩散或是本来的度

冬地受破坏。中国大陆仍然需要进行更多的调查及研究作长时间的监测及保育工作。

越南红河口

2016:9 只

2016 年的普查在红河三角洲只录得 9 只黑脸琵鹭,较 2015 年的数目(44 只)大幅下降了

77.5%。由于与调查日相距不足一周的时间内,调查地点受到了干扰,故此真实的数量

可能比在调查中录得的更高。一如过往的普查,所有的纪录都是在红河三角洲的春水地

区(Xuan Thuy)录得。近年来于红河口度冬黑脸琵鹭的趋势与整个种群数量的趋势不符,

呈下降的趋势,但偶尔有些年份也会出现较高的数量(如: 95-96 年的 75 只)。

日本

2016:383 只

2016 年的普查共于 40 个地点录得黑脸琵鹭(表 1),共录得 383 只黑脸琵鹭,占全球种

群的 11.4%。较 2015 年上升了 3.2%,是破纪录的新高(表 7)。其中熊本县有日本最多

数量的度冬黑脸琵鹭(127 只度冬个体),包括镜川河口录得的 44 只及宇城市的砂川及大

野川河口录得的 21 只。

韩国

2016:38 只

2016 年的普查于韩国济州岛共录得 38 只度冬黑脸琵鹭(下道里有 23 只,城山浦有 15

只),为黑脸琵鹭于韩国的主要度冬地,占全球种群的 1.1%,较 2015 年上升了 23% (31

16

只)。另外,于调查期外有一只黑脸琵鹭纪录于韩国瑞山市。

[菲律宾

2016:0只 (1只在普查以外时间录得)

于调查期间未有纪录到黑脸琵鹭,但是于1月14日有单只纪录。近年,菲律宾偶有录得黑

脸琵鹭,惟该地的水鸟调查工作仍处于起步阶段,很多湿地仍未纳入水鸟调查中。]

[泰国

2016:0只

于整个 2015-16 年度的冬季都没有纪录。近年冬季,似乎有少数黑脸琵鹭幼鸟经常在泰

国海内湾出现。]

总结

今年普查纪录到度冬黑脸琵鹭种群呈 2.5%的轻微上升趋势,自 1993 年开始,除了部分

年份外(2009 及 2011 年),全球种群数量持续上升,每年平均升幅约 11%,但个别地点

的趋势则未必与全球趋势相同。台南地区及日本与全球种群的变化趋势相同,但是过去

十年后海湾及越南红河口纪录到的度冬种群都呈下降趋势,而中国大陆沿海则在不同地

点有个别的上升或下降的趋势。

部分的地点显示了生境管理工作对黑脸琵鹭及其他水鸟有正面的影响,鉴于黑脸琵鹭种

群的上升,故需要扩展整个度冬地区的湿地资源,以容纳更多的黑脸琵鹭度冬种群。故

此,尤其在黑脸琵鹭度冬种群下降,以及有潜力容纳更大度冬种群的地点,湿地管理工

作包括管理措施的计划及实行等极其重要,有利黑脸琵鹭种群在将来的存续。

至于今年的普查中,度冬黑脸琵鹭种群于后海湾地区的数量下降对全球黑脸琵鹭保育响

起警号。米埔自然保护区的管理良好,其管理计划的其中一项就是提供合适生境予度冬

黑脸琵鹭及其他水鸟,包括提供觅食及休息的生境,所以后海湾度冬黑脸琵鹭数量下跌

的原因还未找到。如果我们未能了解影响黑脸琵鹭数量的因素,可能会窒碍全球黑脸琵

鹭数量的恢复。因此,我们提议详细研究黑脸琵鹭在后海湾的生境地利用。

由于全球黑脸琵鹭的数目每年都在变动,普查参考了最近五年的平均数(2,954 只),把

总数 1%订于 30 只的水平。任何地方倘若录得 30 只黑脸琵鹭或以上,均会视作此鸟种

的重要度冬地点,包括:

台湾台南市曾文溪口 – 2016 年有 963 只 (28.7%);

嘉义县南部及台南市北部八掌溪口 – 2016 年有 782 只 (23.3%);

17

香港和深圳后海湾 – 2016 年有 371 只 (11.1%);

台湾高雄 – 2016 年有 186 只 (5.5%);

广东海丰 – 2016 年有 144 只 (4.3%);

福建兴化湾 – 2016 年有 122 只 (4.1%);

台湾鳌鼓湿地 – 2016 年有 88 只 (2.7%);

澳门路凼湿地 – 2016 年有 61 只 (1.6%);

海南岛昌化江口四更 – 2016 年有 47 只 (1.4%)。

日本熊本县镜川河口 – 2016 年有 44 只 (1.3%);

*福建罗源湾 – 2016 年有 38 只 (1.1%);

*广东银湖湾– 2016 年有 31 只 (1.0%)

每年的普查均会涵盖所有曾经录得越冬黑脸琵鹭数目达到总数 1%的地点,以减低遗漏

数算大群黑脸琵鹭的机会。最后两个调查地点(有*者)于今次普查发现其纪录到多于 1%

全球黑脸琵鹭种群,故建议应于未来于此两个地方进行更多的调查以得出其实际的黑

脸琵鹭种群数目及趋势。

18

The International Black-faced Spoonbill Census

2016

黑脸琵鹭全球同步普查 2016

Acknowledgements and References

鸣谢及参考数据

19

Acknowledgments 鸣谢

Counting of spoonbills is indebted to the voluntary efforts by observers who are

experienced bird watchers, conservationists, researchers, ornithologists, government

officers working in reserves and many enthusiastic local volunteers. My heartfelt

gratitude goes to all the observers, data contributors and organizations that

participated and coordinated the census. A list of all participants is appended at the

beginning of this report.

是次普查能顺利完成,全赖有经验的鸟友、保育人士、研究员、鸟类学家、保护区的

政府人员及各地热心调查员等协力收集资料。我们要感谢所有参加野外调查,提供资

料及协助联络或统筹的各位同仁(参加者的名单已在本报告开端列出)。

References 参考数据

BirdLife International. 2015. Platalea minor. The IUCN Red List of Threatened

Species 2015: e.T22697568A84646222.

http://dx.doi.org/10.2305/IUCN.UK.2015.RLTS.T22697568A84646222.en. Downloa

ded on 07 September 2016.

Chan, S. Fang, W.H, Lee, K.S., Yamada, Y. and Yu, Y.T. 2010. International Single

Species Action for the conservation of the Black-faced Spoonbill (Platelea minor).

BirdLife International Asia Division & CMS Secretariat, Tokyo & Bonn, Germany.

Chan K.T. and Yu, Y.T. 2012. International Black-faced Spoonbill Census 2011 & 2012.

Black-faced Spoonbill Research Group, Hong Kong Bird Watching Society. Hong

Kong.

Hancock, J.A., Kushlan, J.A. and Kahl, M.P. 1992. Storks, Ibises and Spoonbills of the

World. Academic Press. London.

del Hoyo, J., Elliott, A. and Saragatal, J. (Eds.). 1992. Handbook of the Birds of the

World Volume 1. Lynx Edicions. Barcelona.

Kennerley, P.R. 1990. A review of the status and distribution of the Black-faced

Spoonbill. Hong Kong Bird Report 1989: 83-100.

Severinghaus, L.L., Brouwer, K., Chan, S. Chong, J.R., Coulter, M.C., Poorter, E.P.R.

and Wang, Y. 1995. Action plan for the Black-faced Spoonbill Platalea minor. “Task

Force to Develop an Action plan for the Preservation of the Black-faced Spoonbill”

Taipei, Taiwan. January 16-22, 1995.

20

Yu, Y.T. 2003. International Black-faced Spoonbill Census: 24-26 January 2003. The

Hong Kong Bird Watching Society. Hong Kong.

Yu, Y.T. and Swennen, C. 2004. Habitat use of the Black-faced Spoonbill. Waterbirds

27(2): 129-134.

21

The International Black-faced Spoonbill Census

2016

黑脸琵鹭全球同步普查 2016

Maps

地图

22

Map 1a. Locations of wintering Black-faced Spoonbills in winter 2015-16.

1) Yamaguchi, Japan; 2) Yamaguchi, Japan; 3) Fukuoka, Japan; 4) Saga, Japan;

5) Kumamoto, Japan; 6) Miyazaki, Japan; 7) Izumi, Japan; 8) Kagoshima, Japan;

9) Seosan City, Republic of Korea; 10) Jeju Island, China; 11) Shanghai, China;

12) Cixi, China.

地图 1a. 2015-16 年黑脸琵鹭冬季栖息地点:

1) 日本东京都; 2) 日本山口县; 3) 日本福冈县; 4) 日本佐贺县;5) 日本熊本县;

6) 日本宫崎县; 7) 日本出水市; 8) 日本鹿儿岛县;9) 韩国瑞山市;10) 韩国济洲岛;

11) 中国上海; 12) 中国慈溪。

23

Map 1b. Locations of wintering Black-faced Spoonbills in winter 2015-16.

A) Okinawa, Japan; B) Ilan County, Taiwan; C) Taipei City, Taiwan;

D) Yunlin County, Taiwan; E) Aogu Wetland, Chiayi County, Taiwan;

F) Penghu County, Taiwan; G) Chiayi County, Taiwan;

H) Tsengwen River estuary, Tainan City, Taiwan; I) Kaohsiung City, Taiwan;

J) Luoyuan Bay, Luoyuan, Fujian; K) Minjiang estuary, Fuzhou, Fujian;

L) Xinhua, Fujian (Fuqing Bay & Xinhua Bay in Putian);

M) Kinmen County, Taiwan; N) Dongshan Bay, Zhangzhou, Fujian;

O) Haifeng, Guangdong; P) Guangzhou, Guangdong;

Q) Deep Bay, Hong Kong and Shenzhen; R) Taipa, Macao;

S) Jiangmen, Guangdong; T) Dongzhaigong, Hainan; U) Lingao, Hainan;

V) Sigang, Hainan; W) Xuan Thuy, Vietnam; X) Thai Thuy IBA, Vietnam;

Y) Candaba, Luzon, The Philippines.

地图 1b. 2015-16 年黑脸琵鹭冬季栖息地点:

A) 日本冲绳群岛; B) 台湾宜兰; C)台湾台北市; D) 台湾云林县;

E) 台湾嘉义县鳌鼓湿地; F) 台湾澎湖县; G) 台湾嘉义县八掌溪口;

H) 台湾台南市曾文溪口 ; I) 台湾高雄市; J) 福建罗源湾; K) 福建闽江口;

L) 福建兴化 (福清湾和莆田兴化湾); M) 台湾金门; N) 福建东山湾;

O) 广东海丰;P) 广东广州; Q) 香港和深圳后海湾; R) 澳门路凼; S) 广东江

门; T) 海南东寨港; U) 海南临高; V) 海南四更; W) 越南红河口春水;

X) 越南泰瑞; Y) 菲律宾吕宋坎达巴。

24

The International Black-faced Spoonbill Census

2016

黑脸琵鹭全球同步普查 2016

Tables

图表

25

Table 1. Number of Black-faced Spoonbills in different locations of East Asia, winter 2015-2016. Numbers in parenthesis are birds counted outside the census period.

表 1. 2015-2016 年冬季东亚各地的黑脸琵鹭数量。括号内的数字为普查期间以外录得

的黑脸琵鹭。 Region

地区

Location

地点 2016

Number

数量

China mainland

中国大陆

Dongtan and Wetland Park, Chongming, Shanghai

上海 祟明 东滩及湿地公园

16 Jan

1 月 16 日

4

China mainland

中国大陆

Cixi, Hangzhou Bay, Zhejiang

浙江 杭州湾 慈溪

19 Jan

1 月 19 日

(8)

China mainland

中国大陆

Luoyuan Bay, Luoyuan, Fujian

福建 罗源 罗源湾

17 Jan

1 月 17 日

38

China mainland

中国大陆

Minjiang estuary, Fuzhou, Fujian

福建 福州 闽江口

15 Jan

1 月 15 日

2

China mainland

中国大陆

Xinhua Bay, Fuqing, Putian, Fujian

福建 福清 莆田 兴化湾

16 Jan

1 月 16 日

122

China mainland

中国大陆

Dongshan Bay, Zhangzhou, Fujian

福建 漳州 东山湾

10 Jan

1 月 10 日

(29)

China mainland

中国大陆

Haifeng, Guangdong

广东 海丰

16 Jan

1 月 16 日

144

China mainland

中国大陆

Nansha, Guangzhou, Guangdong

广东 广州 南沙

15 Jan

1 月 15 日

16

China mainland

中国大陆

Yinhu Bay, Jiangmen, Guangdong

广东 江门 银湖湾

16 Jan

1 月 16 日

31

China mainland

中国大陆

Dongzhaigong, Hainan

海南 东寨港

16 Jan

1 月 16 日

2

China mainland

中国大陆

Xinying, Lingao, Hainan

海南省 临高 新盈

16 Jan

1 月 16 日

28

China mainland

中国大陆

Sigang, Dongfang, Hainan

海南省 东方 四更

16 Jan

1 月 16 日

47

Hong Kong and Shenzhen

香港和深圳

Deep Bay, including Mai Po, Hong Kong and Futian, Shenzhen

后海湾、包括香港米埔及深圳福田

15-17 Jan

1 月 15-17 日

371

Macao

澳门

Taipa-coloane

凼仔-路环

15-17 Jan

1 月 15-17 日

61

Taiwan

台湾

Taipei City

台北市

16 Jan

1 月 16 日

1

Taiwan

台湾

Chiayi County, Aogu Wetland

嘉义县 鳌鼓湿地

16 Jan

1 月 16 日

88

Taiwan

台湾

Chiayi County & Tainan City, Bazheng River estuary

嘉义县及台南市 八掌溪口

16 Jan

1 月 16 日

782

Taiwan

台湾

Tainan City, Tsengwen River estuary, including Chi-ku, Sicao and Tucheng

台南市曾文溪口 包括七股,四草及土城

16 Jan

1 月 16 日

963

Taiwan

台湾

Kaohsiung City, including Qieding and Kaoping River estuary

高雄市 包括茄萣及高屏溪口

16 Jan

1 月 16 日

186

Taiwan

台湾

Yunli County

云林县

16 Jan

1 月 16 日

24

Taiwan

台湾

Ilan County

宜兰县

16 Jan

1 月 16 日

14

Taiwan

台湾

Penghu County

澎湖县

16 Jan

1 月 16 日

1

Taiwan

台湾

Kinmen County

金门县

16 Jan

1 月 16 日

1

26

Japan

日本

Honshu: Tokyo Pref., Edogawa-ku, Tokyo Bay Kasai-rinkai Park.

本州岛岛 东京都 江戸川区 东京湾 葛西临

海公园

17 Jan

1 月 17 日

1

Japan

日本

Honshu: Yamaguchi Pref., Yamaguchi Bay

本州岛岛 山口县 山口市 山口湾周边

17 Jan

1 月 17 日

17

Japan

日本

Kyushu: Kitakyushu City, Suou coast Imagawa River estuary

九州岛岛 北九州岛市 周防滩 今川河口

16 Jan

1 月 16 日

6

Japan

日本

Kyushu: Kitakyushu City, Suou coast Matsuyama reclaimed land

九州岛岛 北九州岛市 周防滩 松山埋立地

16 Jan

1 月 16 日

17

Japan

日本

Kyushu: Fukuoka Pref., Fukutsu City, Tsuyazaki Irie

九州岛岛 福冈县 津屋崎

16 Jan

1 月 16 日

6

Japan

日本

Kyushu: Fukuoka Pref., Fukuoka City, Wajiro tidal flat

九州岛岛 福冈县 福冈市 和白干舄

17 Jan

1 月 17 日

2

Japan

日本

Kyushu: Fukuoka Pref., Fukuoka City, Tatara River estuary

九州岛岛 福冈县 多多良川河口

16 Jan

1 月 16 日

13

Japan

日本

Kyushu: Fukuoka Pref., Fukuoka City, Zuibaiji River estuary, Imazu tidal flat

九州岛岛 福冈县 瑞梅寺川河口 今津干舄

17 Jan

1 月 17 日

18

Japan

日本

Kyushu: Itoshima City, Raizan River

九州岛岛 纟岛市 雷山川

17 Jan

1 月 17 日

3

Japan

日本

Kyushu: Fukuoka Pref., Itoshima City, Izumi River estuary

九州岛岛 福冈县 纟岛市 泉川河口周边

16 Jan

1 月 16 日

13

Japan

日本

Kyushu : Yanagawa City, Okinohata River estuary 九州島 柳川市 沖の端川河口

16 Jan

1 月 16 日

15

Japan

日本

Kyushu : Yanagawa City, Chikugo River estuary & coast

九州岛岛 柳川市 筑后川河口

16 jan

1 月 16 日

2

Japan

日本

Kyushu: Saga Pref., Daijugarami

九州岛岛 佐贺县 大授搦

16 Jan

1 月 16 日

17

Japan

日本

Kyushu: Kashima City, Hama River estuary

九州岛岛 鹿岛市 浜川河口

17 jan

1 月 17 日

12

Japan

日本

Kyushu: Arao City, Arao Tidal flat

九州岛岛 荒尾市 荒尾干舄

17 Jan

1 月 17 日

2

Japan

日本

Kyushu: Nagasu Cho, Nagasu Port

九州岛岛 长洲町 长洲港

17 Jan

1 月 17 日

6

Japan

日本

Kyushu: Nagasu Cho, Ootsutsumi Pond

九州岛岛 长洲町 大堤池

17 Jan

1 月 17 日

8

Japan

日本

Kyushu: Kumamoto Pref., Kikuchi River estuary

九州岛岛 熊本县 菊池川河口

17 Jan

1 月 17 日

15

Japan

日本

Kyushu:Tamana City, Tojin River Estuary

九州岛岛 玉名市 唐人川河口

17 Jan

1 月 17 日

4

Japan

日本

Kyushu: Kumamoto City Ezuko Lake

九州岛岛 熊本市 江津湖

17 Jan

1 月 17 日

2

Japan

日本

Kyushu: Kumamoto Pref., Kumamoto City, Kumamoto Port

九州岛岛 熊本县 熊本市 熊本港

17 Jan

1 月 17 日

13

Japan

日本

Kyushu: Kumamoto Pref., Midori River estuary

九州岛岛 熊本县 绿川河口

17 Jan

1 月 17 日

13

Japan

日本

Kyushu: Kumamoto Pref., Uki City, Ohno River estuary and Suna River estuary

九州岛岛 熊本县 宇城市 大野川河口、砂川河

17 Jan

1 月 17 日

21

27

Japan

日本

Kyushu: Hikawa Cho/Yatsushiro City, Hikawa River Estuary 九州島 熊本県 氷川町・八代市、氷川河口

17 Jan

1 月 17 日

4

Japan

日本

Kyushu: Kumamoto Pref., Kagami River estuary

九州岛岛 熊本县 镜川河口

17 Jan

1 月 17 日

44

Japan

日本

Kyushu: Kumamoto Pref., Mae/Kuma River estuary

九州岛岛 熊本县 前川/球磨河口

17 Jan

1 月 17 日

11

Japan

日本

Kyushu: Miyazaki Pref., Hitotsuse River estuary

九州岛岛 宫崎县 一濑川河口

17 Jan

1 月 17 日

12

Japan

日本

Kyushu: Miyazaki Pref., Kushima City, Tenjin

River 九州岛岛 宫崎县 串间市 天神川

16 Jan

1 月 16 日

5

Japan

日本

Kyushu: Shibushi City, Anraku River estuary

九州岛岛 志布志市 安楽川河口

15 Jan

1 月 15 日

3

Japan

日本

Kyushu: Kagoshima Pref., Kirishima City, HiroseRegulation Pond

九州岛岛 鹿儿岛县 雾岛市 広瀬调整池

15 Jan

1 月 15 日

4

Japan

日本

Kyushu: Kagoshima Pref., Kirishima City, Hamanoichi Irrigation Reservoir

九州岛岛 鹿儿岛县 雾岛市 滨之市调整池

15 Jan

1 月 15 日

14

Japan

日本

Kyushu: Kagoshima Pref., Kajiki Town, Suzaki Irrigation Reservoir

九州岛岛 鹿儿岛县 加治木町 须崎调整池

15 Jan

1 月 15 日

21

Japan

日本

Kyushu: Izumi City, Arasaki

九州岛岛 出水市 荒崎

15 Jan

1 月 15 日

3

Japan

日本

Kyushu: Kagoshima Pref., Minamisatsuma City, Manose River Estuary

九州岛岛 鹿儿岛县 南萨摩市 万之瀬川河口

17 Jan

1 月 17 日

15

Japan

日本

Kyushu: Kagoshima Pref., Minamisatsuma City, Ohura Reclamation Area

九州岛岛 鹿儿岛县 南萨摩市 大浦干拓周边

17 Jan

1 月 17 日

2

Japan

日本

Nansei-shoto Islands: Naha City/Tomigusuku City, Man-ko Tidal flat

南西诸岛 那覇市/豊见城市 漫湖干舄

17 Jan

1 月 17 日

2

Japan

日本

Nansei-shoto Islands: Okinawa Pref., Tomigusuku, Yone-Sankaku-ike Pond

西南诸岛 冲绳县 与根三角池

17 Jan

1 月 17 日

2

Japan

日本

Nansei-shoto Islands: Okinawa Pref., Tomigusuku, Toyosaki tidal flat

西南诸岛 冲绳县 豊见城 豊崎干舄

17 Jan

1 月 17 日

13

Japan

日本

Nansei-shoto Islands: Okinawa Pref., Haneji Naikai tidal flat

南西诸岛 冲绳县 羽地内海

17 Jan

1 月 17 日

2

Republic of Korea

韩国

Jeju: Hado-ri fishponds

济州 下道里 鱼塘

16 Jan

1 月 16 日

23

Republic of Korea

韩国

Jeju: Seongsanpo

济州 城山浦

16 Jan

1 月 16 日

15

Republic of Korea

韩国

South Chungcheong Province: Haemi Stream, Seosan City

忠清南道 瑞山市

22 Jan

1 月 22 日

(1)

Vietnam

越南

Red River Delta, Xuan Thuy National Park

红河口 春水国家公园

17 Jan

1 月 17 日

8

Vietnam

越南

Thai Thuy

泰瑞

16 Jan

1 月 16 日

1

The Philippines

菲律宾 Candaba, Luzon 吕宋 坎达巴 15-17 Jan

1 月 15-17 日

(1)

Total 总数: 3,356 (3,395)

28

Table 2. Sites visited with no Black-faced Spoonbill counted during or near the 2016 census period.

表 2. 2016 年全球同步普查期间曾进行调查但未有录得琵鹭的地方。 Region

地区

Location

地点 2016

China mainland

中国大陆

Nanhui, Shanghai

上海 南汇

16 Jan

1 月 16 日

China mainland

中国大陆

Quanzhou Bay, Fujian

福建 泉州湾

16 Jan

1月16日

China mainland

中国大陆

Xiamen, Fujian

福建 厦门

16 Jan

1 月 16 日

China mainland

中国大陆

Qi’ao Island, Zhuhai, Guangdong

广东 珠海 淇澳岛

16-17 Jan

1 月 16-17 日

China mainland

中国大陆

Zhanjiang, Guangdong

广东 湛江

16-17 Jan

1 月 16-17 日

China mainland

中国大陆

Beihai, Guangxi

广西 北海

17 Jan

1 月 17 日

China mainland

中国大陆

Sanya, Hainan

海南 三亚

15-17 Jan

1 月 15-17 日

Taiwan

台湾

Changhua County

彰化县

16 Jan

1 月 16 日

Taiwan

台湾

Hualien County

花莲县

16 Jan

1 月 16 日

Taiwan

台湾

Taitung County

台东县

16 Jan

1 月 16 日

Taiwan

台湾

Taichung City

台中市

16 Jan

1 月 16 日

Taiwan

台湾

Matsu Islands

马祖

16 Jan

1 月 16 日

Japan

日本

Honshu: Ibaraki Pref., Kamisu City Hasaki Tone River Estuary

本州岛岛 茨城県 神栖市波崎 利根川河口

15 Jan

1 月 15 日

Japan

日本

Kyushu: Kitakyushu City, Suou coast Kanda regulation pond

九州岛岛 北九州岛市 周防滩 苅田调整池

16 Jan

1 月 16 日

Japan

日本

Kyushu: Kitakyushu City, Suou coast Sone shore

九州岛岛 北九州岛市 周防滩 曾根海岸

16 Jan

1 月 16 日

Japan

日本

Kyushu: Itoshima City, Fukuryu Pond etc.

九州岛岛 纟岛市 伏龙池

17 Jan

1 月 17 日

Japan

日本

Kyushu: Saga City, Hayatsue River estuary

九州岛岛 佐贺市 早津江川河口

16 Jan

1 月 16 日

Japan

日本

Kyushu: Kashima City, Hizen-Kashima Tidal flat (Shingomori)

九州岛岛 鹿岛市 肥前鹿岛干舄(新笼)

17 Jan

1 月 17 日

Japan

日本

Kyushu: Kashima City, Nanaura Shioya coast

九州岛岛 鹿岛市 七浦塩屋

17 Jan

1 月 17 日

Japan

日本

Kyushu: Kashima City, Nanaura Iida Fishery port

九州岛岛 鹿岛市 饭田渔港

17 Jan

1 月 17 日

Japan

日本

Kyushu: Isahaya City, Isahaya Bay

九州岛岛 谏早市 谏早湾

16 Jan

1 月 16 日

Japan

日本

Kyushu: Soo County, Oosaki Cho, Hishida River estuary

九州岛岛 曽于郡大崎町 菱田川河口

16 Jan

1 月 16 日

Japan

日本

Kyushu: Kimotsuki County, Oosaki Cho, Tabaru River estuary

九州岛岛 曽于郡大崎町 田原川河口

16 Jan

1 月 16 日

29

Japan

日本

Kyushu: Soo County, Oosaki Cho, Kimotsuki River estuary

九州岛岛 曽于郡大崎町 肝属川河口

16 Jan

1 月 16 日

Japan

日本

Kyushu: Aira City, Matsubara Regulation Pond

九州岛岛 姶良市 松原调整池

15 Jan

1 月 15 日

Japan

日本

Nansei-shoto Islands: Okinawa Pref., Gushi tidal flat

南西诸岛 冲绳县 具志干舄

17 Jan

1 月 17 日

Japan

日本

Nansei-shoto Islands: Itoman City, Komesu Coast

南西诸岛 纟満市 米洲海岸

17 Jan

1 月 17 日

Japan

日本

Nansei-shoto Islands: Nago City, Ooura Bay-Teima River estuary 南西諸島 名護市 大浦湾ー汀間川河口

17 Jan

1 月 17 日

Japan

日本

Nansei-shoto Islands: Nago City, Teniya Coast

南西诸岛 名护市 天仁屋海岸

17 Jan

1 月 17 日

Japan

日本

Nansei-shoto Islands: Oogimison, Shioya Bay

南西诸岛 大宜味村 塩屋湾

17 Jan

1 月 17 日

Japan

日本

Nansei-shoto Islands: Uruma City, Uminaka Road

南西诸岛 宇流麻 海中道路

17 Jan

1 月 17 日

Thailand

泰国

Khao Takrao, Petchaburi

碧武里

15-17 Jan

1 月 15-17 日

30

Table 3. Numbers of Black-faced Spoonbills in Taiwan during the international censuses.

表 3. 全球同步普查期间在台湾录得的黑脸琵鹭数量。 Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00 Jan 01

Total 150 206 286 300 298 363 380 380 427

Year Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08 Jan 09

Total 582 580* 632 757 826 790 1030 1104

Year Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Total 1280 834 1562 1624 1659 2034 2060

* This number also included the 18 sick individuals infected by avian botulism. 此数字包括 18 只受鸟类

肉毒杆菌感染的黑脸琵鹭。

Table 4. Numbers of Black-faced Spoonbills in the Pearl River Estuary during the international censuses.

表 4. 全球同步普查期间在珠江河口录得的黑脸琵鹭数量。 Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00

Hong Kong 50 70 78 99 69 88 96 90

Shenzhen nc nc nc nc 32 58 nc nc

Macao 6 12 8 10 13 9 12 6

Total 56 82 86 109 114 155 108 96

Year Jan 01 Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08

Hong Kong 135 136 179 238 272 296 320 331

Shenzhen 42* 3 24 5 39 50 36 38

Macao 36 37 46 50 39 51 48 50

Total 171* 176 249 293 350 397 404 419

Year Jan 09 Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Hong Kong 273 429 386 357 322 222 363 322

Shenzhen 62 33 25 36 29 30 48 49

Macao 52 39 49 51 48 60 55 61

Total 387 501 460 444 399 312 466 432

nc = no count 未有进行调查

*Forty-two birds in Futian were not included in the total number because counts in Mai Po and

Futian were not taken simultaneously. 因米埔与福田的调查未能与同步进行,故总数未有包括

42 只在福田录得的黑脸琵鹭。

31

Table 5. Numbers of Black-faced Spoonbills in China mainland (excludes Futian, Shenzhen) and Hainan Island during the international censuses.

表 5. 全球同步普查期间在中国大陆(不包括深圳福田)及海南岛录得的黑脸琵鹭数量。

Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00

Total 15 22 21 21 58 5 3 9

Year Jan 01 Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08

Total 72 24 17 91 187 206 247 313

Year Jan 09 Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Total 247 234 198 328 363 339 330 434

Table 6. Numbers of Black-faced Spoonbills in Red River Delta, Vietnam during the international censuses.

表 6. 全球同步普查期间在越南红河口录得的黑脸琵鹭数量。

Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00

Total 62 25 23 75 nc 59 34* 46*

Year Jan 01 Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08

Total 47 54* 65 62 56 74 45 49

Year Jan 09 Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Total 63 46 49 35 39 40 40 9

nc = no count 未有进行调查

* Surveys also included Thai Binh and other places in the Delta. 普查地点包括 Thai Binh 及红

河口内的其他地点。

Table 7. Numbers of Black-faced Spoonbills in Japan during the international censuses.

表 7. 全球同步普查期间在日本录得的黑脸琵鹭数量。 Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00

Total 5 16 14 31 28 75 60 99

Year Jan 01 Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08

Total 87 107 128 149 103 (150*) 155 189 224

Year Jan 09 Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan15 Jan 16

Total 215 258 270 284 277 350 371 383

*The figure of 150 included 47 individuals recorded outside the census period but they were likely staying in Japan for the whole winter.

32

Table 8. Numbers of Black-faced Spoonbills in Jeju Island, Republic of Korea during the international censuses.

表 8. 全球同步普查期间在韩国济州岛录得的黑脸琵鹭数量。 Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00

Total 6 nc nc 15 16 25 14 20

Year Jan 01 Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08

Total 21 29 22 23 21 21 20 28

Year Jan 09 Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Total 25 27 26 40 23 26 31 38

Table 9. Numbers and percentage increase of total number of Black-faced Spoonbills during the international censuses.

表 9. 全球同步普查的黑脸琵鹭总数及百分比增加。 Year 89-90 93-94 94-95 95-96 Jan 97 Jan 98 Jan 99 Jan 00

Total 294 351 430 551 535 613 586 660

% change - 19.4 22.5 28.1 -2.9 14.6 -4.4 12.6

Year Jan 01 Jan 02 Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08

Total 828 969 1069 1206 1475 1679 1695 2065

% change 25.5 17.0 10.3 12.8 22.3 13.8 1.0 21.8

Year Jan 09 Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Total 2041 2347 1839 2693 2725 2726 3272 3356

% change -1.2 15.0 -21.6 46.4 1.2 0.04 20.0 2.57

Annual % change (SD) from 1989 to 2016: 11.0%

1989 年至 2016 年间的年均变化:11.0%

Table 10. Number of survey sites in past censuses.

表 10. 历年全球同步普查调查地点的数目。 Year Jan 03 Jan 04 Jan 05 Jan 06 Jan 07 Jan 08 Jan 09

Number of sites recorded BFS

36 39 40 40 44 43 44

Number of survey site

41 61 61 59 68 No detail record

No detail record

Year Jan 10 Jan 11 Jan 12 Jan 13 Jan 14 Jan 15 Jan 16

Number of sites recorded BFS

52 56 56 53 62 62 68

Number of survey site

82 83 86 67 96 91 94

33

The International Black-faced Spoonbill Census 2016

黑脸琵鹭全球同步普查 2016

Figures 图片

34

Figure 1 Known wintering Black-faced Spoonbill populations from winter 1989-90 to 2015-16.

图 1. 1989-90 至 2015-16 年冬季已知的黑脸琵鹭数量。

Figure 2. Percentages of Black-faced Spoonbills in different wintering areas during the 2016 international census.

图 2. 2016 全球同步普查期间黑脸琵鹭在不同越冬地的全球百分比。

35

Figure 3. A comparison of the trends of the known global population of Black-faced Spoonbill at main wintering areas.

图 3. 比较七个主要越冬地区的已知黑脸琵鹭数量趋势。

36

The International Black-faced Spoonbill Census 2016

黑脸琵鹭全球同步普查 2016

Appendix

附录

37

Appendix 1. Counts of Black-faced Spoonbills in Hong Kong and Shenzhen during the International Black-faced Spoonbill Census 2016.

附录 1. 2016 年黑脸琵鹭全球同步普查香港及深圳结果。 a) 15 January 2016 / 2016 年 1 月 15 日

Place 地点 /Time 时间 1300h 1400h 1500h 1600h

Mai Po Nature Reserve and

boardwalk 米埔自然护理区及浮桥 80 84 83 60

Lok Ma Chau 落马洲 40 38 42 45

San Tin 新田 0 0 0 0

Mai Po San Tsuen 米埔新村 7 0 0 0

Tai Sang Wai 大生围 25 3 24 0

Tam Kon Chau 担竿洲 0 0 0 0

Nam Sang Wai 南生围 1 0 1 5

Tsim Bei Tsui area, including Wetland

Park 尖鼻咀 (包括湿地公园) 89 93 90 23

Futian 福田 22 32 36 42

Total 总数 257 250 276 175

b) 16 January 2016 / 2016 年 1 月 16 日

Place 地点 /Time 时间 1330h 1430h 1530h 1630h

Mai Po Nature Reserve and

boardwalk 米埔自然护理区及浮桥 79 101 80 79

Lok Ma Chau 落马洲 2 0 22 46

San Tin 新田 0 0 0 0

Mai Po San Tsuen 米埔新村 0 0 0 0

Tai Sang Wai 大生围 0 17 19 17

Tam Kon Chau 担竿洲 0 0 0 0

Nam Sang Wai 南生围 0 0 0 0

Tsim Bei Tsui area, including Wetland

Park 尖鼻咀 (包括湿地公园) 108 105 106 96

Futian 福田 42 38 34 30

Total 总数 231 261 261 268

c) 17 January 2016 / 2016 年 1 月 17 日

Place 地点 /Time 时间 1430h 1530h 1630h 1730h

Mai Po Nature Reserve and

boardwalk 米埔自然护理区及浮桥 81 101 56 118

Lok Ma Chau 落马洲 85 42 70 NA

San Tin 新田 1 0 2 0

Mai Po San Tsuen 米埔新村 27 31 36 24

Tai Sang Wai 大生围 4 7 7 0

Tam Kon Chau 担竿洲 0 0 0 0

Nam Sang Wai 南生围 14 4 4 5

Ma Tso Lung 马草垄 2 6 0 0

Tsim Bei Tsui area, including Wetland

Park 尖鼻咀 (包括湿地公园) 108 111 112 93

Futian 福田 49 45 50 42

Total 总数 371 347 337 282